solt stateocdimage.emnrd.state.nm.us/imaging/filestore/artesia/ao/...2016/04/06  · solt state work...

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March 1, 2016 NMOCD District II Attn. Heather Patterson 1301 W Grand Ave Artesia, NM 88210 SUBJECT: SOIL REMEDIATION WORK PLAN FOR INCIDENT 2RP1167 Solt State, API# 3001525277, EDDY COUNTY, NEW MEXICO Dear Ms. Patterson: On behalf Alamo Permian Resources, Souder Miller & Associates (SMA) is pleased to submit the attached Work Plan summarizing the soil remediation planned for the release site located on the Solt in Eddy County, New Mexico. The purpose of the work plan is to obtain approval from the New Mexico Oil Conservation Division for remediation of the release that occurred on June 6, 2012. At the request of Alamo Permian Resources, SMA assessed and delineated the produced water release associated with the Solt State well location. The release was initially reported to NMOCD by COG Operating on June 6, 2012 and was a result of a poly flowline leak incident. The table below summarizes information regarding the release. Results of the assessment and delineation follow in the attached report. Table 1: Release information and Site Ranking Name Solt State Location Incident Number API Number Section, Township, Range 2RP1167 3001525277 SW/SE (UL O) Section 5 T 18S, R 28E NMPM Estimated Date of Release June 6, 2012 Date Reported to NMOCD June 6, 2012 Reported by Tom Fulvi, Alamo Permian Resources Land Owner New Mexico State Land Office Reported To NM Oil Conservation Division (NMOCD) Source of Release Poly Flow Line Leak Released Material Produced Water Released Volume 150 bbls Produced Water Recovered Volume 0 bbls Produced Water Net Release 150 bbls Produced Water Nearest Waterway 1.8 miles West of the location. Depth to Groundwater Estimated to be 95 feet

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Page 1: Solt Stateocdimage.emnrd.state.nm.us/Imaging/FileStore/Artesia/AO/...2016/04/06  · Solt State Work Plan SMA Ref 5B24270 BG 7 03/1/16 between the affected soils and the proposed caliche

 

 

 

March 1, 2016    NMOCD District II Attn. Heather Patterson  1301 W Grand Ave Artesia, NM 88210  SUBJECT: SOIL REMEDIATION WORK PLAN FOR INCIDENT 2RP‐1167 Solt State, API# 30‐015‐25277, EDDY COUNTY, NEW MEXICO  Dear Ms. Patterson:  On behalf Alamo Permian Resources, Souder Miller & Associates (SMA) is pleased to submit the attached Work Plan summarizing the soil remediation planned for the release site located on the Solt in Eddy County, New Mexico. The purpose of the work plan is to obtain approval from the New Mexico Oil Conservation Division for remediation of the release that occurred on June 6, 2012.   At the request of Alamo Permian Resources, SMA assessed and delineated the produced water release associated with the Solt State well location.  The release was initially reported to NMOCD by COG Operating on June 6, 2012 and was a result of a poly flowline leak incident. The table below summarizes information regarding the release.  Results of the assessment and delineation follow in the attached report.  

Table 1: Release information and Site Ranking 

Name  Solt State

Location 

Incident Number

API Number

Section, Township, Range 

2RP‐1167 

30‐015‐25277 

SW/SE (UL O) 

Section 5 

T 18S, R 28E NMPM 

Estimated Date of Release  June 6, 2012 

Date Reported to NMOCD  June 6, 2012 

Reported by  Tom Fulvi, Alamo Permian Resources 

Land Owner  New Mexico State Land Office 

Reported To  NM Oil Conservation Division (NMOCD)  

Source of Release  Poly Flow Line Leak 

Released Material  Produced Water 

Released Volume  150 bbls Produced Water 

Recovered Volume   0 bbls Produced Water 

Net Release   150 bbls Produced Water 

Nearest Waterway  1.8 miles West of the location.   

Depth to Groundwater  Estimated to be 95 feet  

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Nearest Domestic Water Source  Greater than 1000 feet 

NMOCD Ranking  10 

SMA Response Dates  Initial: 02/17/16 Mitigation Activities: Unknown 

Subcontractors  MSI 

A copy of the C‐141 Initial is located in Appendix B.  For questions or comments pertaining to the release or the attached Work Plan, please feel free to contact either of us.  Submitted by: Reviewed by: SOUDER, MILLER & ASSOCIATES

Austin Weyant Cynthia Gray, CHMM Project Scientist Senior Scientist

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SOIL REMEDIATION WORK PLAN FOR INCIDENT 2RP-1167

ALAMO PERMIAN RESOURCES SOLT STATE

API# 30-015-25277 UL O SECTION 5, T18S R28E, NMPM

EDDY COUNTY, NM

 

Prepared for: Alamo Permian Resources 415 West Wall St Midland, TX 79701

Prepared by: Souder, Miller & Associates 201 S. Halagueno Carlsbad, NM 88221 575-689-7040

March 1, 2016 SMA Reference 5B24270 BG7

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Table of Contents  

1.0  Introduction ...................................................................................................................................... 4 

2.0  Site Ranking and Land Jurisdiction ............................................................................................. 4 

3.0  Assessment and Initial Results .................................................................................................... 4 

4.0  Soil Remediation Work Plan ......................................................................................................... 4 

5.0  Conclusions and Recommendations ........................................................................................... 5 

6.0  Closure and Limitations ................................................................................................................. 5 

Figures: 

Figure 1: Vicinity Map Figure 2: Site Map Figure 3: In-situ Cap and Bio barrier Design Tables:

Table 1: Release Information and Site Ranking Table 2: Summary of Laboratory Analyses Appendices:

Appendix A: Laboratory Analytical Reports Appendix B: Form C141 INITIAL Appendix C: API Amigo Summary

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1.0 Introduction

On behalf of Alamo Permian Resources (Alamo), Souder Miller and Associates (SMA) has prepared this report that describes the assessment and initial delineation of a release associated with the Solt State #1, API #30-015-25277, well site. The site is located in Section 5, T 18S, R 28 E NMPM, Eddy County, New Mexico, on land owned by the New Mexico State Land Office. Figure 1 illustrates the vicinity and location of the site.

2.0 Site Ranking and Land Jurisdiction

The Solt State #1 release site is located approximately 7 miles (> 1,000 feet) east of Pecos River, in an area administered by New Mexico State Land Office with an elevation of approximately 3,640 feet above sea level. After evaluation of the site using aerial photography and topographic maps, depth to groundwater is estimated to be less than 100 feet but greater than 50 feet below ground surface (bgs). Figure 1 depicts the site vicinity and Figure 2 depicts the site details and sample locations. SMA searched the New Mexico State Engineer’s Office online water well database for water wells in the vicinity of the release. No well is located within a 1000 foot radius of the site. Figure 1 depicts the site vicinity and Figure 2 shows the site itself. The physical location of this release is within the jurisdiction of NMOCD. This release location has been assigned a NMOCD ranking of 10 which requires a soil remediation standard of 10 parts per million (ppm) benzene, 50 ppm combined benzene, toluene, ethyl-benzene, and total xylenes (BTEX), and 1000 ppm total petroleum hydrocarbons (TPH). Table 1 illustrates site ranking rationale.

3.0 Assessment and Initial Results

On February 17, 2016, after receiving 811 clearance, SMA field personnel assessed the release area onsite with a backhoe and Bobcat auger, a Photo Ionization Detector (PID), and a mobile chlorides titration kit. The affected area was found to be 372 feet long and 177 feet wide. Delineation samples were taken to depths of six feet bgs. Using field screening, samples at six foot bgs were found to exhibit elevated levels of chloride. Initial assessment activities did not show chloride results below NMOCD guidelines. Sample locations are noted on Figure 2 Site Details and Sample Location Map. All samples were collected and processed according to NMOCD soil sampling procedures. The samples were sent under chain-of-custody protocols to Hall Environmental Analysis Laboratory for analysis for Benzene and Total BTEX using EPA Method 8021B, DRO and GRO by EPA Method 8015D, and total Chlorides using EPA Method 300.0.

4.0 Soil Remediation Work Plan

SMA has determined that the impacted area was previously excavated to approximately one foot bgs during initial response activities. SMA proposes to mobilize a hollow stem auger HSA to the location to continue vertical delineation, final samples well be collected delimiting the impacted area. The in-situ cap will be placed over the delineated impacted area to encompass the horizontal extent of the impact. The cap will consist of bentonite and geotextile layer and two feet of soil. The construction of the in-situ cap (Figure #3) has been designed to prevent both capillary and leaching movement of the brine affected soils. Starting at surface grade the affected soils will be compacted and amended with a bentonite impregnated geotextile liner to act as a capillary break

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between the affected soils and the proposed caliche cap. Then 2 feet of top soil will be added above the geotextile liner. The geotextile liner on the bottom of the top soil will effectively break the communication of precipitation through the cap. The imported topsoil will be added as over burden to help with contouring to prevent ponding and pooling on the cap area. Any contaminated soil will be transported to Lea Land, near Carlsbad, NM. 5.0 Conclusions and Recommendations NMOCD Guidelines for Remediation of Leaks, Spills, and Releases have established the following action levels for contaminants of concern with a site ranking of 10: 10 ppm (mg/kg) Benzene, 50 ppm total BTEX, and 1000 ppm TPH. The release consisted of produced and associated petroleum found during the initial assessment and delineation. SMA will finish delineating on a vertical extent with samples collected for lab confirmation. After the soil remediation work plan is approved by NMOCD, SMA will begin soil remediation activities on site. Soil contaminant concentrations found during the initial delineation are illustrated in Figure 2. A summary of the laboratory analyses is included in Table 2. Laboratory reports are included in Appendix A.

6.0 Closure and Limitations

The scope of our services consisted of the performance of a preliminary spill assessment, verification of release stabilization, regulatory liaison, and preparation of this Remediation Work Plan. All work has been performed in accordance with generally accepted professional environmental consulting practices for oil and gas releases in the Permian Basin in New Mexico. If there are any questions regarding this report, please contact either Austin Weyant at 575-689-7040 or Cindy Gray at 505-325-7535. Submitted by: Reviewed by: SOUDER, MILLER & ASSOCIATES

Austin Weyant Cynthia Gray, CHMM Project Scientist Senior Scientist

 

 

 

 

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Figures: 

Figure 1: Vicinity Map Figure 2: Site Details and Sample Locations Map Figure 3: In-situ Cap and Bio barrier Design Tables:

Table 1: Release Information and Site Ranking Table 2: Summary of Laboratory Analyses Appendices:

Appendix A: Laboratory Analytical Reports Appendix B: Form C141 Initial Appendix C: API Amigo Summary

 

   

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FIGURE 1

VICINITY MAP

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Vicinity MapAlamo Permian Resources- Solt State

Artesia, New MexicoFigure 1

201 South Halaguena StreetCarlsbad, New Mexico 88221

(575) 689-7040www.soudermiller.com

Serving the Southwest & Rocky MountainsDocu

ment:

C:\U

sers\

lcm\D

ocum

ents\

GIS D

ATA\M

APS\F

igure

1 Solt

State

.mxd

Date Sa

ved:

3/9/20

16

DrawnCheckedApproved

By:By:

Date:Date:

Descr:Descr:

Revisions

Copyright 2015 Souder, Miller & Associates - All Rights Reserved

Lucas Middleton

N0 3 61.5 Miles

LegendLocation

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FIGURE 2

SITE DETAILS AND SAMPLE LOCATIONS MAP

 

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L6

L5

L4

L3

L2

L1

Site Detail and Sample LocationsAlamo Permin Resources -Solt State

Artesia, New MexicoFigure 2

201 South Halaguena StreetCarlsbad, New Mexico 88221

(575) 689-7040www.soudermiller.com

Serving the Southwest & Rocky MountainsDocu

ment:

C:\U

sers\

lcm\D

ocum

ents\

GIS D

ATA\M

APS\F

igure

2 Solt

State

.mxd

Date Sa

ved:

3/9/20

16

DrawnCheckedApproved

By:By:

Date:Date:

Descr:Descr:

Revisions

Copyright 2015 Souder, Miller & Associates - All Rights Reserved

Lucas Middleton

N0 80 16040 Feet

LegendSampleEstimated Affected AreaIn-situ Cap Area

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FIGURE 3

IN-SITU CAP AND BIO BARRIER DESIGN

 

 

 

 

 

 

 

 

 

 

 

 

 

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Horiz:Scale:

Project No:

Vert:

Date:

T:\5-Alamo Permian Saunders A No.2 (5B24270)\BG7 - Solt State #001\Figure 3.dwg, LCM, 2/25/2016 3:58 PM© Copyright 2015 Souder, Miller & Associates - All Rights Reserved

Souder, Miller & Associates

Serving the Southwest & Rocky Mountains

www.soudermiller.com

Phone (575) 689-7040

201 S. Halaqueno StreetCarlsbad, NM 88220

February 2016

Figure 3

IN-SITU CAP

AND BIOBARRIER DESIGN

Alamo Premian Resources- Solt State

COG

NA

NA

LMGJF

KT

5B24270

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TABLE 1

RELEASE INFORMATION AND SITE RANKING

   

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Name

Incident

Number

API

Number

2RP-116730-015-

25277

SW/SE (UL

O)Section 5

T 18S, R 28E

NMPM

Estimated Date of Release

Date Reported to NMOCD

Reported by

Land Owner

Reported To

Source of Release

Released Material

Released Volume

Recovered Volume

Net Release

Nearest Waterway

Depth to Groundwater

Nearest Domestic Water Source

NMOCD Ranking

SMA Response Dates

Subcontractors

June 6, 2012

Table 1: Release information and Site Ranking

Solt State

Location

Section, Township, Range

June 6, 2012

Initial: 02/17/16 Mitigation Activities: Unknown

MSI

10

Tom Fulvi, Alamo Permian Resources

NM Oil Conservation Division (NMOCD)

Equipment error

Produce Water

150 bbls Produce Water

New Mexico State Land Office

0 bbls Produce Water

150 bbls Produce Water

1.8 miles West of the location.

Estimated to be 95 feet

Greater than 1000 feet

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TABLE 2

SUMMARY OF LABORATORY ANALYSES

   

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Analytical

Report- BTEX Benzene GRO DRO Cl-

1602A13 ppm mg/Kg mg/Kg mg/Kg mg/Kg

1602A13-

001L1 2/17/2016 1' BDL BDL BDL BDL 1,100

1602A13-

002L1 2/17/2016 6' N/A N/A N/A N/A 14,000

1602A13-

003L4 2/17/2016 3' N/A N/A N/A N/A 470

1602A13-

004L4 2/17/2016 6' N/A N/A N/A N/A 440

1602A13-

005L5 2/17/2016 2' BDL BDL BDL BDL 1,200

1602A13-

006L5 2/17/2016 6' N/A N/A N/A N/A 7,200

1602A13-

007L6 2/17/2016 3' N/A N/A N/A N/A 49

Table 2: Summary of Laboratory Analyses

Sample

Number on

Figure 2 Map

Sample Date Depth

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APPENDIX A

LABORATORY ANALYTICAL REPORTS

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March 03, 2016

Souder, Miller & AssociatesAustin Weyant

Dear Austin Weyant:

RE: Solt State OrderNo.: 1602A13

FAXTEL: (575) 689-7040

201 S HalaguenoCarlsbad, NM 88221

Hall Environmental Analysis Laboratory4901 Hawkins NE

Albuquerque, NM 87109

Website: www.hallenvironmental.comTEL: 505-345-3975 FAX: 505-345-4107

Hall Environmental Analysis Laboratory received 7 sample(s) on 2/24/2016 for the analyses presented in the following report.

Andy Freeman

These were analyzed according to EPA procedures or equivalent. To access our accredited tests please go to www.hallenvironmental.com or the state specific web sites. In order to properly interpret your results it is imperative that you review this report in its entirety. See the sample checklist and/or the Chain of Custody for information regarding the sample receipt temperature and preservation. Data qualifiers or a narrative will be provided if the sample analysis or analytical quality control parameters require a flag. When necessary, data qualifers are provided on both the sample analysis report and the QC summary report, both sections should be reviewed. All samples are reported, as received, unless otherwise indicated. Lab measurement of analytes considered field parameters that require analysis within 15 minutes of sampling such as pH and residual chlorine are qualified as being analyzed outside of the recommended holding time.

Please don't hesitate to contact HEAL for any additional information or clarifications.

ADHS Cert #AZ0682 -- NMED-DWB Cert #NM9425 -- NMED-Micro Cert #NM0190

Sincerely,

Laboratory Manager4901 Hawkins NEAlbuquerque, NM 87109

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Project: Solt StateClient Sample ID: L1-1

Collection Date: 2/17/2016 8:00:00 AMMatrix: SOIL

CLIENT: Souder, Miller & Associates

Lab ID: 1602A13-001

Date Reported: 3/3/2016

Analytical ReportLab Order 1602A13

Analyses Result Qual Units Date AnalyzedDFPQL

Hall Environmental Analysis Laboratory, Inc.

Received Date: 2/24/2016 10:05:00 AM

Batch

EPA METHOD 300.0: ANIONS Analyst: LGTChloride 2/26/2016 4:17:46 PM30 mg/Kg 201100 23978

EPA METHOD 8015M/D: DIESEL RANGE ORGANICS Analyst: KJHDiesel Range Organics (DRO) 2/26/2016 4:51:12 PM94 mg/Kg 101400 23916

Motor Oil Range Organics (MRO) 2/26/2016 4:51:12 PM470 mg/Kg 10720 23916

Surr: DNOP S 2/26/2016 4:51:12 PM70-130 %Rec 100 23916

EPA METHOD 8015D: GASOLINE RANGE Analyst: NSBGasoline Range Organics (GRO) 2/25/2016 8:57:50 PM4.9 mg/Kg 19.8 23925

Surr: BFB S 2/25/2016 8:57:50 PM66.2-112 %Rec 1152 23925

EPA METHOD 8021B: VOLATILES Analyst: NSBBenzene 2/25/2016 8:57:50 PM0.049 mg/Kg 1ND 23925

Toluene 2/25/2016 8:57:50 PM0.049 mg/Kg 1ND 23925

Ethylbenzene 2/25/2016 8:57:50 PM0.049 mg/Kg 1ND 23925

Xylenes, Total 2/25/2016 8:57:50 PM0.098 mg/Kg 1ND 23925

Surr: 4-Bromofluorobenzene 2/25/2016 8:57:50 PM80-120 %Rec 1116 23925

Qualifiers:

Page 1 of 11

Refer to the QC Summary report and sample login checklist for flagged QC data and preservation information.

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

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Project: Solt StateClient Sample ID: L1-6

Collection Date: 2/17/2016 8:00:00 AMMatrix: SOIL

CLIENT: Souder, Miller & Associates

Lab ID: 1602A13-002

Date Reported: 3/3/2016

Analytical ReportLab Order 1602A13

Analyses Result Qual Units Date AnalyzedDFPQL

Hall Environmental Analysis Laboratory, Inc.

Received Date: 2/24/2016 10:05:00 AM

Batch

EPA METHOD 300.0: ANIONS Analyst: LGTChloride 3/1/2016 9:51:23 PM750 mg/Kg 50014000 23978

Qualifiers:

Page 2 of 11

Refer to the QC Summary report and sample login checklist for flagged QC data and preservation information.

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

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Project: Solt StateClient Sample ID: L4-3

Collection Date: 2/17/2016 8:00:00 AMMatrix: SOIL

CLIENT: Souder, Miller & Associates

Lab ID: 1602A13-003

Date Reported: 3/3/2016

Analytical ReportLab Order 1602A13

Analyses Result Qual Units Date AnalyzedDFPQL

Hall Environmental Analysis Laboratory, Inc.

Received Date: 2/24/2016 10:05:00 AM

Batch

EPA METHOD 300.0: ANIONS Analyst: LGTChloride 2/26/2016 3:40:33 PM30 mg/Kg 20470 23978

Qualifiers:

Page 3 of 11

Refer to the QC Summary report and sample login checklist for flagged QC data and preservation information.

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

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Project: Solt StateClient Sample ID: L4-6

Collection Date: 2/17/2016 8:00:00 AMMatrix: SOIL

CLIENT: Souder, Miller & Associates

Lab ID: 1602A13-004

Date Reported: 3/3/2016

Analytical ReportLab Order 1602A13

Analyses Result Qual Units Date AnalyzedDFPQL

Hall Environmental Analysis Laboratory, Inc.

Received Date: 2/24/2016 10:05:00 AM

Batch

EPA METHOD 300.0: ANIONS Analyst: LGTChloride 2/26/2016 4:55:01 PM30 mg/Kg 20440 23978

Qualifiers:

Page 4 of 11

Refer to the QC Summary report and sample login checklist for flagged QC data and preservation information.

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

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Project: Solt StateClient Sample ID: L5-2

Collection Date: 2/17/2016 8:00:00 AMMatrix: SOIL

CLIENT: Souder, Miller & Associates

Lab ID: 1602A13-005

Date Reported: 3/3/2016

Analytical ReportLab Order 1602A13

Analyses Result Qual Units Date AnalyzedDFPQL

Hall Environmental Analysis Laboratory, Inc.

Received Date: 2/24/2016 10:05:00 AM

Batch

EPA METHOD 300.0: ANIONS Analyst: LGTChloride 2/26/2016 5:07:27 PM30 mg/Kg 201200 23978

EPA METHOD 8015M/D: DIESEL RANGE ORGANICS Analyst: KJHDiesel Range Organics (DRO) 2/26/2016 5:34:39 PM10 mg/Kg 1ND 23916

Motor Oil Range Organics (MRO) 2/26/2016 5:34:39 PM51 mg/Kg 1ND 23916

Surr: DNOP 2/26/2016 5:34:39 PM70-130 %Rec 173.8 23916

EPA METHOD 8015D: GASOLINE RANGE Analyst: NSBGasoline Range Organics (GRO) 2/25/2016 9:21:25 PM4.8 mg/Kg 1ND 23925

Surr: BFB 2/25/2016 9:21:25 PM66.2-112 %Rec 194.1 23925

EPA METHOD 8021B: VOLATILES Analyst: NSBBenzene 2/25/2016 9:21:25 PM0.048 mg/Kg 1ND 23925

Toluene 2/25/2016 9:21:25 PM0.048 mg/Kg 1ND 23925

Ethylbenzene 2/25/2016 9:21:25 PM0.048 mg/Kg 1ND 23925

Xylenes, Total 2/25/2016 9:21:25 PM0.096 mg/Kg 1ND 23925

Surr: 4-Bromofluorobenzene 2/25/2016 9:21:25 PM80-120 %Rec 1110 23925

Qualifiers:

Page 5 of 11

Refer to the QC Summary report and sample login checklist for flagged QC data and preservation information.

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

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Project: Solt StateClient Sample ID: L5-6

Collection Date: 2/17/2016 8:00:00 AMMatrix: SOIL

CLIENT: Souder, Miller & Associates

Lab ID: 1602A13-006

Date Reported: 3/3/2016

Analytical ReportLab Order 1602A13

Analyses Result Qual Units Date AnalyzedDFPQL

Hall Environmental Analysis Laboratory, Inc.

Received Date: 2/24/2016 10:05:00 AM

Batch

EPA METHOD 300.0: ANIONS Analyst: LGTChloride 3/1/2016 10:03:48 PM300 mg/Kg 2007200 23979

Qualifiers:

Page 6 of 11

Refer to the QC Summary report and sample login checklist for flagged QC data and preservation information.

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

Page 26: Solt Stateocdimage.emnrd.state.nm.us/Imaging/FileStore/Artesia/AO/...2016/04/06  · Solt State Work Plan SMA Ref 5B24270 BG 7 03/1/16 between the affected soils and the proposed caliche

Project: Solt StateClient Sample ID: L6-3

Collection Date: 2/17/2016 8:00:00 AMMatrix: SOIL

CLIENT: Souder, Miller & Associates

Lab ID: 1602A13-007

Date Reported: 3/3/2016

Analytical ReportLab Order 1602A13

Analyses Result Qual Units Date AnalyzedDFPQL

Hall Environmental Analysis Laboratory, Inc.

Received Date: 2/24/2016 10:05:00 AM

Batch

EPA METHOD 300.0: ANIONS Analyst: LGTChloride 2/29/2016 12:28:02 PM30 mg/Kg 2049 23979

Qualifiers:

Page 7 of 11

Refer to the QC Summary report and sample login checklist for flagged QC data and preservation information.

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

Page 27: Solt Stateocdimage.emnrd.state.nm.us/Imaging/FileStore/Artesia/AO/...2016/04/06  · Solt State Work Plan SMA Ref 5B24270 BG 7 03/1/16 between the affected soils and the proposed caliche

Project: Solt StateClient: Souder, Miller & Associates

09-Mar-16

QC SUMMARY REPORT 1602A13WO#:Hall Environmental Analysis Laboratory, Inc.

Sample ID MB-23978

Batch ID: 23978

Analysis Date: 2/26/2016Prep Date: 2/26/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: PBS RunNo: 32456

SeqNo: 992631

MBLKSampType: TestCode: EPA Method 300.0: Anions

Chloride 1.5ND

Sample ID LCS-23978

Batch ID: 23978

Analysis Date: 2/26/2016Prep Date: 2/26/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: LCSS RunNo: 32456

SeqNo: 992632

LCSSampType: TestCode: EPA Method 300.0: Anions

Chloride 15.00 95.8 90 1101.5 014

Sample ID MB-23979

Batch ID: 23979

Analysis Date: 2/29/2016Prep Date: 2/29/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: PBS RunNo: 32483

SeqNo: 993599

MBLKSampType: TestCode: EPA Method 300.0: Anions

Chloride 1.5ND

Sample ID LCS-23979

Batch ID: 23979

Analysis Date: 2/29/2016Prep Date: 2/29/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: LCSS RunNo: 32483

SeqNo: 993600

LCSSampType: TestCode: EPA Method 300.0: Anions

Chloride 15.00 95.2 90 1101.5 014

Qualifiers:

Page 8 of 11

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

Page 28: Solt Stateocdimage.emnrd.state.nm.us/Imaging/FileStore/Artesia/AO/...2016/04/06  · Solt State Work Plan SMA Ref 5B24270 BG 7 03/1/16 between the affected soils and the proposed caliche

Project: Solt StateClient: Souder, Miller & Associates

09-Mar-16

QC SUMMARY REPORT 1602A13WO#:Hall Environmental Analysis Laboratory, Inc.

Sample ID LCS-23916

Batch ID: 23916

Analysis Date: 2/26/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: LCSS RunNo: 32421

SeqNo: 991462

LCSSampType: TestCode: EPA Method 8015M/D: Diesel Range Organics

Diesel Range Organics (DRO) 50.00 84.3 65.8 13610 042

Surr: DNOP 5.000 91.1 70 1304.6

Sample ID MB-23916

Batch ID: 23916

Analysis Date: 2/26/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: PBS RunNo: 32421

SeqNo: 991464

MBLKSampType: TestCode: EPA Method 8015M/D: Diesel Range Organics

Diesel Range Organics (DRO) 10ND

Motor Oil Range Organics (MRO) 50ND

Surr: DNOP 10.00 92.6 70 1309.3

Sample ID 1602996-001AMS

Batch ID: 23916

Analysis Date: 2/26/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: BatchQC RunNo: 32422

SeqNo: 991875

MSSampType: TestCode: EPA Method 8015M/D: Diesel Range Organics

Diesel Range Organics (DRO) 47.80 146 31.2 1629.6 070

Surr: DNOP 4.780 127 70 1306.1

Sample ID 1602996-001AMSD

Batch ID: 23916

Analysis Date: 2/26/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: BatchQC RunNo: 32422

SeqNo: 991951

MSDSampType: TestCode: EPA Method 8015M/D: Diesel Range Organics

Diesel Range Organics (DRO) 49.65 147 31.2 162 31.79.9 0 4.7973

Surr: DNOP 4.965 119 70 130 005.9

Qualifiers:

Page 9 of 11

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

Page 29: Solt Stateocdimage.emnrd.state.nm.us/Imaging/FileStore/Artesia/AO/...2016/04/06  · Solt State Work Plan SMA Ref 5B24270 BG 7 03/1/16 between the affected soils and the proposed caliche

Project: Solt StateClient: Souder, Miller & Associates

09-Mar-16

QC SUMMARY REPORT 1602A13WO#:Hall Environmental Analysis Laboratory, Inc.

Sample ID MB-23925

Batch ID: 23925

Analysis Date: 2/25/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: PBS RunNo: 32403

SeqNo: 991237

MBLKSampType: TestCode: EPA Method 8015D: Gasoline Range

Gasoline Range Organics (GRO) 5.0ND

Surr: BFB 1000 92.8 66.2 112930

Sample ID LCS-23925

Batch ID: 23925

Analysis Date: 2/25/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: LCSS RunNo: 32403

SeqNo: 991238

LCSSampType: TestCode: EPA Method 8015D: Gasoline Range

Gasoline Range Organics (GRO) 25.00 105 79.6 1225.0 026

Surr: BFB 1000 97.3 66.2 112970

Sample ID 1602A03-003AMS

Batch ID: 23925

Analysis Date: 2/25/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: BatchQC RunNo: 32403

SeqNo: 991245

MSSampType: TestCode: EPA Method 8015D: Gasoline Range

Gasoline Range Organics (GRO) 23.99 118 59.3 1434.8 028

Surr: BFB 959.7 102 66.2 112980

Sample ID 1602A03-003AMSD

Batch ID: 23925

Analysis Date: 2/25/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: BatchQC RunNo: 32403

SeqNo: 991246

MSDSampType: TestCode: EPA Method 8015D: Gasoline Range

Gasoline Range Organics (GRO) 24.04 119 59.3 143 204.8 0 1.2829

Surr: BFB 961.5 102 66.2 112 00980

Qualifiers:

Page 10 of 11

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

Page 30: Solt Stateocdimage.emnrd.state.nm.us/Imaging/FileStore/Artesia/AO/...2016/04/06  · Solt State Work Plan SMA Ref 5B24270 BG 7 03/1/16 between the affected soils and the proposed caliche

Project: Solt StateClient: Souder, Miller & Associates

09-Mar-16

QC SUMMARY REPORT 1602A13WO#:Hall Environmental Analysis Laboratory, Inc.

Sample ID MB-23925

Batch ID: 23925

Analysis Date: 2/25/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: PBS RunNo: 32403

SeqNo: 991270

MBLKSampType: TestCode: EPA Method 8021B: Volatiles

Benzene 0.050ND

Toluene 0.050ND

Ethylbenzene 0.050ND

Xylenes, Total 0.10ND

Surr: 4-Bromofluorobenzene 1.000 111 80 1201.1

Sample ID LCS-23925

Batch ID: 23925

Analysis Date: 2/25/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: LCSS RunNo: 32403

SeqNo: 991271

LCSSampType: TestCode: EPA Method 8021B: Volatiles

Benzene 1.000 100 80 1200.050 01.0

Toluene 1.000 104 80 1200.050 01.0

Ethylbenzene 1.000 104 80 1200.050 01.0

Xylenes, Total 3.000 105 80 1200.10 03.2

Surr: 4-Bromofluorobenzene 1.000 116 80 1201.2

Sample ID 1602A03-001AMS

Batch ID: 23925

Analysis Date: 2/25/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: BatchQC RunNo: 32403

SeqNo: 991274

MSSampType: TestCode: EPA Method 8021B: Volatiles

Benzene 0.9634 89.3 71.5 1220.048 00.86

Toluene 0.9634 98.3 71.2 1230.048 00.95

Ethylbenzene 0.9634 105 75.2 1300.048 01.0

Xylenes, Total 2.890 108 72.4 1310.096 03.1

Surr: 4-Bromofluorobenzene 0.9634 116 80 1201.1

Sample ID 1602A03-001AMSD

Batch ID: 23925

Analysis Date: 2/25/2016Prep Date: 2/24/2016

Analyte Result SPK value SPK Ref Val %REC %RPDLowLimit HighLimit RPDLimit Qual

Units: mg/Kg

PQL

Client ID: BatchQC RunNo: 32403

SeqNo: 991275

MSDSampType: TestCode: EPA Method 8021B: Volatiles

Benzene 0.9643 87.3 71.5 122 200.048 0 2.230.84

Toluene 0.9643 95.5 71.2 123 200.048 0 2.780.92

Ethylbenzene 0.9643 98.3 75.2 130 200.048 0 6.560.95

Xylenes, Total 2.893 102 72.4 131 200.096 0 5.143.0

Surr: 4-Bromofluorobenzene 0.9643 118 80 120 001.1

Qualifiers:

Page 11 of 11

* Value exceeds Maximum Contaminant Level. B Analyte detected in the associated Method BlankD Sample Diluted Due to Matrix E Value above quantitation rangeH Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits

ND Not Detected at the Reporting Limit P Sample pH Not In RangeR RPD outside accepted recovery limits RL Reporting Detection LimitS % Recovery outside of range due to dilution or matrix W Sample container temperature is out of limit as specified

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Solt State Work Plan  SMA Ref 5B24270 BG 7 

03/1/16 

  

 

 

 

 

 

APPENDIX B

FORM C141 INITIAL

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District I 1625 N. French Dr., Hobbs, NM 88240 District II 811 S. First St., Artesia, NM 88210 District III 1000 Rio Brazos Road, Aztec, NM 87410 District IV 1220 S. St. Francis Dr., Santa Fe, NM 87505

State of New Mexico Energy Minerals and Natural Resources

Oil Conservation Division 1220 South St. Francis Dr.

Santa Fe, NM 87505

Form C-141 Revised August 8, 2011

Submit 1 Copy to appropriate District Office in accordance with 19.15.29 NMAC.

Release Notification and Corrective Action

Name of Company A L A M O PERMIAN RESOUCES, LLC Contact STEVEN MASTIN Address 415 W. WALL ST. SUITE 500 Telephone No. 432 557 5847 Facility Name SOLT STATE Facility Type BATTERY

Surface Owner STATE Mineral Owner STATE API No. 30-015-25277

LOCATION OF RELEASE

0 Section Township Range Feet from the North/South Line Feet from the EastAVest Line County

0 5 18S 28E 660 S 1980 E EDDY

Latitude 32.7705300 Longitude-104.1952600

NATURE OF RELEASE Type of Release: PRODUCED WATER Volume of Release: 150 BBLS WATER Volume Recovered: 0 Source of Release: FLOW LINE LEAK Date and Hour of Occurrence: JUNE 6, 2012 Date and Hour of Discovery

JUNE 6,2012 Was Immediate Notice Given?*

Required • Not

If YES, To Whom? STEVEN MASTIN

By Whom? RICKY RODRIGUEZ, FIELD SUPERVISOR Date and Hour JUNE 6, 2012, 1:30 PM Was a Watercourse Reached?

• Yes _3 No If YES, Volume Impacting the Watercourse.

If a Watercourse was Impacted, Describe Fully.*

RECEIVED Describe Cause of Problem and Remedial Action Taken.*

Cause of problem: Flowline leak at wellsite location; Scraping up and hauling to Gandy Marley. JUN 0 7 2012 Describe Area Affected and Cleanup Action Taken.'

Clean up action: To be determined based on environmental assessment. NMOCD ARTESIA

I hereby certify that the information given above is true and complete to the best of my knowledge and understand that pursuant to NMOCD rules and regulations all operators are required to report and/or file certain release notifications and perform corrective actions for releases which may endanger public health or the environment. The acceptance of a C-141 report by the NMOCD marked as "Final Report" does not relieve the operator of liability should their operations have failed to adequately investigate and remediate contamination that pose a threat to ground water, surface water, human health or the environment. In addition, NMOCD acceptance of a C-141 report does not relieve the operator of responsibility for compliance with any other federal, state, or local laws and/or regulations.

Signature:

Printed Name: TOM FULVI

OIL CONSERVATION DIVISION

WAS A&#f2zScJ?t_-Signed By_ Approved by Environmental Specialist:

Title: REGULATORY/ PRODUCTION TECH Approval Date: JUN 1 3 2012 Expiration Date:

E-mail Address: [email protected]

Date: 0673

06/06//20I2 Phone: 432 897

* Attach Additional Sheets I f Necessary

Conditions of Approval:

Remediation per OCD Rules & Guidelines. SUBMIT REMEDIATION

Attached •

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Solt State Work Plan  SMA Ref 5B24270 BG 7 

03/1/16 

  

APPENDIX C

API AMIGO SUMMARY

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AMIGO

http://amigo-app.api.org/default.aspx[3/2/2016 3:27:02 PM]

AMIGO

no file selected

Units

Metric (m) English (inches)

Climate

Arid Hot (NM/W.Texas, Hobbs)

Input for a Distant Well

Distance to Well [ft]

Source Width [ft]

Longitudinal Dispersivity [-]

Transverse Dispersivity [-]

Groundwater Characterictics

Background CI Concentration

in Aquifer cGW = [mg/L]

Aquifer porosity n = [-]

Groundwater Table Depth D = 10 [ft]

Aquifer Thickness H = [ft]

Slope of Water Table i = [-]

Hydraulic Conductivity Ks = [ft/d]

Groundwater Flux Q = [ft2/d]

Source Characteristics

Chloride Load: Max. length of the spill in

direction of GW flow:

M = [kg/m2] L = [ft]

Plant Uptake Trigger

1% Input Concentration

10% Input Concentration

Soil Profiles

Surface Layer

Medium Sand

Soil Profile

P4 - Caliche (1) + Medium Sand (5)

Output Charts

Quantity 1: Chloride concentration [g/kg]

Legend

Quantity 2: Conc. at an Adjacent Well [mg/L]

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